Esther
Welcome to the group. You are correct that the figures you provided showed a problem in fitting detection function models to the data as depicted. Were the data recorded in the field using the cutpoints you describe (<30, 30-100, >100)? If so, there is little
that can be done to remedy the situation. Modelling point count data is difficult when recording exact distances; it is much more difficult with the broad (0-30m) first bin for the reason you describe. It is the shape of the fitted detection function at small
distances that is central to producing sound estimates from point transect data. I don't think either of your suggested remedies will be of use.
Regarding your second point, point transect surveys assume availability of animals increases linearly as a function of distance from the point; i.e. the number of animals available to be detected increases as the area of the detection bands increases. Existence
of hedgerows creates a discontinuity in this linear availability function. Adding a covariate to the detection function model will not solve this problem. The problem is reduced if there are a large number of replicate transects (~20), lessening the influence
of a particular habitat feature on the data set. Non-linearity of the availability curve at large distances can be mitigated by truncation (see Buckland 2006), but with three distance bands your truncation options are extremely limited.
As you note, your ability to fit parameter-rich models is impeded by the number of bins into which your data were collected. In any event, a multi-modal detection function is not the answer to the problem, because it is not detectability that is changing because
of the hedgerow, instead it is the availability of animals that is changing.
If you have the opportunity to repeat the survey, collecting detections using exact distances enhances your modelling opportunities. Also having sufficient replicate transects can diminish the influence of some types of availability features.